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Committee of the Whole/Documents/Attachment 7 - Construction Impact Assessment & Tree Management Plan
Appendix

Attachment 7 - Construction Impact Assessment & Tree Management Plan

June 14, 2022Pages 89–10013 sections

A detailed arborist report assessing the impact of construction on existing trees and providing management recommendations.

7.2.3.b Development Permit Application No. 2021/02 - 167, 169 and 171 Island Highway
June 18, 2021Amended May 19, 2022Talmack Urban Forestry Consultants Ltd.3 urban lots (167, 169 & 171 Island Hwy)Inventory identifies bylaw protected and municipal trees

167, 169 & 171 Island Hwy, View Royal, BC

Page 89–100

Construction Impact Assessment & Tree Management Plan

PREPARED FOR: GT Mann Contracting Ltd. 1551 Broadmead Ave Victoria, BC V8P 2V1

PREPARED BY: Talmack Urban Forestry Consultants Ltd. Graham Mackenzie – Consulting Arborist ISA Certified # PN-0428A Tree Risk Assessment Qualified

DATE OF ISSUANCE: June 18, 2021 Amended May 19, 2022


Page 89–100

CONTENTS

  1. INTRODUCTION ............................................................................................................................ 1
  2. TREE INVENTORY METHODOLOGY ........................................................................................... 1
  3. EXECUTIVE SUMMARY ................................................................................................................ 1
  4. TREE INVENTORY DEFINITIONS ................................................................................................. 2
  5. SITE INFORMATION & PROJECT UNDERSTANDING ................................................................ 9
  6. FIELD OBSERVATIONS ................................................................................................................ 9
  7. TREE RISK ASSESSMENT ........................................................................................................... 9
  8. CONSTRUCTION IMPACT ASSESSMENT ................................................................................. 10 8.1. Retention and Removal of Municipal Trees .................................................................................. 10 8.2. retention and removal of private offsite trees ............................................................................... 10 8.3. retention and removal of onsite trees ........................................................................................... 11 8.4. tree replacement ........................................................................................................................... 11
  9. IMPACT MITIGATION .................................................................................................................. 11
  10. DISCLOSURE STATEMENT ........................................................................................................ 13
  11. IN CLOSING ................................................................................................................................. 14
  12. REFERENCES ............................................................................................................................. 15

TABLES Table 1. Tree Inventory ........................................................................................................................................ 4

APPENDICES Appendix A Tree Management Plan (T1) Appendix B Site Photographs


Page 89–100

1. INTRODUCTION

Talmack Urban Forestry Consultants was asked to complete a tree inventory, construction impact assessment and management plan for the trees at the following proposed project:

  • Site: 167, 169 & 171 Island Hwy,
  • Municipality: View Royal, BC
  • Client Name: GTMann Contracting Ltd.
  • Dates of Site Visit: May 20, 2021
  • Site Conditions: 3 urban lots. No ongoing construction activity. Gradual increase in elevation from South to North.
  • Weather During Site Visit: Clear and sunny

The purpose of this report is to address requirements of the Town of View Royal Tree Preservation Bylaw No. 695. The construction impact assessment section of this report (section 8), is based on plans reviewed to date, including the Architectural site, foundation, floor & Elevation plans (May 18, 2021) - Prepared by Urban West Architecture. At this time we have not reviewed a civil servicing plan (showing proposed underground utility connection locations), or a landscape plan.

Page 89–100

2. TREE INVENTORY METHODOLOGY

Prior to our site visit, we were provided with surveyed tree locations from the project surveyor (Wey Mayenburg Land Surveying Inc.). For the purpose of this report, the size, health, and structural condition of trees was documented. For ease of identification in the field, numerated metal tags were attached to the lower trunks of onsite trees. Trees located on neighbouring properties, the municipal frontage or in areas where access was restricted, were not tagged (identified as NT 1 – NT 11). Each tree was visually examined on a limited visual assessment basis (level 1), in accordance with Tree Risk Assessment Qualification (TRAQ) methods (Dunster et al. 2017) and ISA Best Management Practices.

Page 89–100

3. EXECUTIVE SUMMARY

Based on review of the architectural site, foundation, floor & Elevation plans provided, we anticipate that the majority of the onsite trees and some trees on neighbouring properties located close to the property line will require removal. The tree management plan (T1) in appendix A) shows trees that we anticipate will require removal and those that we feel can be retained, providing their critical root zones can be adequately protected during construction. In order to complete the excavation for the underground portion of the building and retain trees on neighbouring properties it may require shoring techniques to minimise the requirements for any cut slopes. This will depend on the soil conditions, the depth of excavation and the requirements from the geotechnical engineer.

Page 89–100

4. TREE INVENTORY DEFINITIONS

Tag: Tree identification number on a metal tag attached to tree with nail or wire, generally at eye level. Trees on municipal or neighboring properties are not tagged.

NT: No tag due to inaccessibility or ownership by municipality or neighbour.

DBH: Diameter at breast height – diameter of trunk, measured in centimetres at 1.4m above ground level. For trees on a slope, it is taken at the average point between the high and low side of the slope. * Measured over ivy ~ Approximate due to inaccessibility or on neighbouring property

Dripline: Indicates the radius of the crown spread measured in metres to the dripline of the longest limbs.

Relative Tolerance Rating: Relative tolerance of the tree species to construction related impacts such as root pruning, crown pruning, soil compaction, hydrology changes, grade changes, and other soil disturbance. This rating does not take into account individual tree characteristics, such as health and vigour. Three ratings are assigned based on our knowledge and experience with the tree species: Poor (P), Moderate (M) or Good (G).

Critical Root Zone: A calculated radial measurement in metres from the trunk of the tree. It is the optimal size of tree protection zone and is calculated by multiplying the DBH of the tree by 10, 12 or 15 depending on the tree’s Relative Tolerance Rating. This methodology is based on the methodology used by Nelda Matheny and James R. Clark in their book “Trees and Development: A Technical Guide to Preservation of Trees During Land Development.”

  • 15 x DBH = Poor Tolerance of Construction
  • 12 x DBH = Moderate
  • 10 x DBH = Good

To calculate the critical root zone, the DBH of multiple stems is considered the sum of 100% of the diameter of the largest stem and 60% of the diameter of the next two largest stems. It should be noted that these measures are solely mathematical calculations that do not consider factors such as restricted root growth, limited soil volumes, age, crown spread, health, or structure (such as a lean).

Health Condition:

  • Poor - significant signs of visible stress and/or decline that threaten the long-term survival of the specimen
  • Fair - signs of stress
  • Good - no visible signs of significant stress and/or only minor aesthetic issues

Structural Condition:

  • Poor - Structural defects that have been in place for a long period of time to the point that mitigation measures are limited
  • Fair - Structural concerns that are possible to mitigate through pruning
  • Good - No visible or only minor structural flaws that require no to very little pruning

Suitability ratings are described as follows:

Rating: Suitable.

  • A tree with no visible or minor health or structural defects, is tolerant to changes to the growing environment and is a possible candidate for retention provided that the critical root zone can be adequately protected.

Rating: Conditional.

  • A tree with good health but is a species with a poor tolerance to changes to its growing environment or has a structural defect(s) that would require that certain measures be implemented, in order to consider it suitable for retention (ie. retain with other codominant tree(s), structural pruning, mulching, supplementary watering, etc.)

Rating: Unsuitable.

  • A tree with poor health, a major structural defect (that cannot be mitigated using ANSI A300 standards), or a species with a poor tolerance to construction impacts, and unlikely to survive long term (in the context of the proposed land use changes).

Retention Status:

  • Remove - Not possible to retain given proposed construction plans
  • Retain - It is possible to retain this tree in the long-term given the proposed plans and information available. This is assuming our recommended mitigation measures are followed
  • Retain * - See report for more information regarding potential impacts

Table 1. Tree Inventory

Page 89–100
Prev Tag. Tag or ID # Bylaw protected ? Common Name Botanical Name dbh (cm) CRZ r (m) Ht (m) Dripline diameter (m) Health Condition Structural Condition Relative tolerance General field observations/remarks
473 yes Grand fir Abies grandis 53 6.5 20 6 Fair/good Fair Poor Codomimant leaders form at 15 meters above grade, small deadwood in canopy.
869 474 yes Bigleaf maple Acer macrophyllum 51, 18 7 20 9 Fair/good Fair/poor Moderate Secondary stem forms at .5m above grade - narrow angle of attachment, fruiting bodies between stem union.
866 yes Western redcedar Thuja plicata 14 - 38 4 10 8 Fair Fair/good Moderate Hedge row consisting of 15 Western redcedar amd 24 Leyland Cypress.
M1 yes Garry oak Quercus garryanna 6 1 5 1 Good Fair/good Good Juvenile tree, codomimant leaders form at 3m above grade. Hasn’t fully established - some root plate movement.
M2 yes Garry oak Quercus garryanna 5 1 5 1 Good Good Good Juvenile tree, hasn’t fully established - some root plate movement.
M3 yes Linden Tilia cordata 18 2 10 6 Good Fair Moderate Included bark at brands unions.
M4 yes Eddies white wonder dogwood Cornus nuttalli x florida 7 1 4 3 Fair/poor Fair Moderate Health stress - sparse crown.
M5 yes Linden Tilia cordata 18 2 10 6 Good Fair Moderate Included bark at brands unions.
873 475 yes Purple leaf plum Prunus cerasifera 26, 14, 9 3 8 8 Good Fair Good Growing within close proximity to existing retaining wall on North side, previous stem failures.
876 476 yes Bigleaf maple Acer macrophyllum 52 6 15 12 Good Fair Moderate Codomimant leaders form at 8m above grade - included and active union, injured surface root.
477 yes Garry oak Quercus garryanna 64 6 20 18 Good Fair/good Good Balanced crown, some endweighted limbs.
478 yes Douglas-fir Pseudotsuga menziesii 60 7 20 10 Fair/poor Fair Poor Health stress - twig amd branch dieback, surface rooted.
479 yes Arbutus Arbutus menziesii 24, 14, 13 4 10 8 Fair/good Fair Poor Multiple stems cluster, suppressed by 478 - asymmetric crown on West side due to shading.
480 yes Western red cedar Thuja plicata 50 5 20 8 Poor Fair/good Moderate Declining health - top dieback - 50%lcr.
NT1 yes Spruce Picea species 25 3 15 5 Fair Fair/poor Poor Deflected top, secondary leader.
481 yes Golden Chain Tree Laburnum 16, 16, 15 3 10 7 Fair Fair/poor Moderate Deadwood, included bark in unions.
482 yes Plum Prunus species 28, 25, 20, 18, 16, ~15, ~15, ~12, ~10 5 12 14 Fair Fair/poor Good Multiple stems, some leaning, deadwood, ivy on trunks, included bark.
483 yes Cherry Prunus species 44 4 20 12 Fair/poor Fair/poor Moderate Health stress, deadwood, tortrix infestation, leans east, supported by 484.
484 yes Grand fir Abies grandis 52 6 30 11 Fair Fair Poor Lower trunk wound.
OS1 yes Grand fir Abies grandis 37 4 20 8 Fair Fair Poor Surface roots, sparse foliage lower crown.
OS2 yes Douglas-fir Pseudotsuga menziesii 32 4 20 9 Fair Fair Poor Deadwood lower crown, branch failures (hangers).
485 yes Katsura Cercidiphyllum japonica 13, 13, 12, 12, 11 3 10 8 Good Fair/poor Good Multiple stems with narrow attachments arising in close proximity, included bark.
NT2 no Red Alder Unus rubra 29 3.5 15 10 Good Fair Poor Large surface root.
NT3 no Plum Prunus species 14, 14, 9 3 5 5 Fair Fair/poor Moderate Large surface root, topping/heading cuts historically.
486 yes Leyland Cypress Cupressus x leylandii 46, 44, 36 4 20 12 Good Fair/poor Good Tridominant, included bark.
487 yes Deodar Cedar Cedrus deodara 42 4 25 10 Good Fair Moderate Some yellowing/browning foliage, canopy competition with 488.
488 yes Leyland Cypress Cupressus x leylandii 50 5 20 10 Good Fair Good East end of hedge row, asymmetric crown due to competition.
OS3 yes Bigleaf maple Acer macrophyllum 50, 25 6 20 14 Poor Poor Moderate Extensive decay, undermined, large epicormic growth, supported by hedge row. Wildlife tree sign affixed.
NT4 no Leyland Cypress Cupressus x leylandii 25 3 15 7 Good Fair Good Part of hedge row, asymmetric due to competition.
489 yes Leyland Cypress Cupressus x leylandii 38, 24 4 20 9 Good Fair/poor Good Codominant, included bark primary union.
OS4 yes European Hornbeam Carpinus betulus 57, 33 at 0.75m 6 15 12 Good Fair Moderate Multiple stems arising from close points of attachment characteristic of species.
NT5 no Leyland Cypress Cupressus x leylandii 29 3 15 7 Good Fair Good Part of hedge row, asymmetric due to competition.
490 yes Leyland Cypress Cupressus x leylandii 36 3.5 15 8 Good Fair Good Part of hedge row, asymmetric due to competition.
491 yes Leyland Cypress Cupressus x leylandii 34 3.5 15 8 Good Fair Good Part of hedge row, asymmetric due to competition.
492 yes Leyland Cypress Cupressus x leylandii 37 3.5 15 8 Good Fair Good Part of hedge row, asymmetric due to competition.
493 yes Leyland Cypress Cupressus x leylandii 27, 17 3.5 15 10 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Codominant, included bark.
495 yes Leyland Cypress Cupressus x leylandii 39, 22 4 15 12 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Codominant, included bark.
NT6 no Leyland Cypress Cupressus x leylandii 24 3 15 8 Good Fair Good Part of hedge row, asymmetric due to competition.
495 yes Leyland Cypress Cupressus x leylandii 29, 25, 22 4 15 9 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Tridominant, included bark, roots heaving driveway?
496 yes Leyland Cypress Cupressus x leylandii 28, 25 4 15 8 Fair Fair/poor Good Part of hedge row, asymmetric due to competition. Structure suggests previous topping. Codominant, included bark.
NT7 no Leyland Cypress Cupressus x leylandii 26 3 10 7 Fair/poor Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
497 yes Leyland Cypress Cupressus x leylandii 38 3 15 7 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
498 yes Leyland Cypress Cupressus x leylandii 32 3 15 7 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
499 yes Leyland Cypress Cupressus x leylandii 25, 16 3 15 7 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
500 yes Leyland Cypress Cupressus x leylandii 32 3 15 8 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
NT8 no Leyland Cypress Cupressus x leylandii 27 3 15 7 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
NT9 no Leyland Cypress Cupressus x leylandii 28 3 15 7 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
436 yes Leyland Cypress Cupressus x leylandii 30 3 15 8 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
NT10 no Leyland Cypress Cupressus x leylandii 29 3 15 8 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
437 yes Leyland Cypress Cupressus x leylandii 38 4 15 8 Good Fair/poor Good Part of hedge row, asymmetric due to competition. Topped historically.
438 yes Leyland Cypress Cupressus x leylandii 40 4 15 8 Good Fair/poor Good North end of hedge row. Topped historically, long seam of included bark in attachment between codominant leaders.
NT11 yes Leyland Cypress Cupressus x leylandii 22avg. 3 15 7 Fair Fair/poor Good Seven stems in hedge row, asymmetric due to competition. Topped historically.
Page 89–100

*CRZ calculated above and drawn as follows on Tree Management Plan (T1): CRZ + 0.5 * d.b.h. (drawn from the center of the stem)


Page 89–100

5. SITE INFORMATION & PROJECT UNDERSTANDING

The development site consists of three urban lots (167, 169 & 171 Island Hwy), in View Royal, B.C., which have existing residences situated on the lots. It is our understanding that the proposal is to remove the existing residences and create a multi-unit building with underground parking.

Below is a general observation of the tree resource, as it appeared at the time of our site visit:

Page 89–100

6. FIELD OBSERVATIONS

The onsite tree resource consists of a mixture of native and ornamental species. The site is bordered by municipal parkland to the South and East and a commercial property to the West.

Site context air photo showing 167, 169, and 171 Island Hwy boundaries outlined in yellow
Site context air photo showing 167, 169, and 171 Island Hwy boundaries outlined in yellow

figure 1: Site context air photo: The boundaries of the subject site is outlined in Yellow.

Page 89–100

7. TREE RISK ASSESSMENT

During our May 20, 2021 site visit and in conjunction with the tree inventory, onsite trees were assessed for risk, on a limited visual assessment basis (level 1), and in the context of the existing land uses. The time frame used for the purpose of our assessment is one year (from the date of the May 20, 2021 tree inventory). Unless otherwise noted herein, we did not conduct a detailed (level 2) or advanced (level 3) risk assessment, such as resistograph testing, increment core sampling, aerial examinations, or subsurface root/root collar examinations.

Existing Land Uses

We did not observe any trees that were deemed to be moderate, high or extreme risk (in the context of the existing land uses, that would require hazard abatement to eliminate present and/or future risks (within a 1-year timeframe). Targets considered during this TRAQ assessment include: occupants of the existing residence (constant use), occupants of vehicles travelling on Island Hwy (frequent use), pedestrians travelling along existing sidewalks (frequent use), hydro lines (constant use).


Page 89–100

8. CONSTRUCTION IMPACT ASSESSMENT

8.1. RETENTION AND REMOVAL OF MUNICIPAL TREES

The following municipal trees (indicated by ID #) are located where it is possible for retention providing that its critical root zones are adequately protected during construction. The project arborist must be onsite to supervise and excavation or fill placement required within its critical root zone (shown on the tree management plan (T1) in appendix A):

Retain and protect 1 municipal trees

  • M1 – M5

*Note that the municipality will need to provide consent, prior the removal of any trees that are located on Municipal property.

8.2. RETENTION AND REMOVAL OF PRIVATE OFFSITE TREES

The following private offsite tree (indicated by ID #) are located where it will be heavily impacted by excavation and blasting required to construct the foundation of the proposed residence and is proposed for removal:

Remove 3 trees located on neighboring property.

  • OS1 – OS3

*Prior written consent from the neighbouring owner is required prior to the removal of any trees located on neignbouring properties. Unsurveyed trees may require surveying to verify ownership.

The following Private offsite tree (indicated by ID #) are located where it is possible for retention providing that its critical root zones are adequately protected during construction. The project arborist must be onsite to supervise and excavation or fill placement required within its critical root zone (shown on the tree management plan (T1) in appendix A):

Retain and protect 1 offsite tree

  • OS4
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Extracted from: 2022 06 14 Committee of the Whole Agenda - Agenda - Pdf